Iowa DNR
Iowa DNR
ADBNet
Water Quality Assessments
Impaired Waters List

Roberts Creek IA 01-TRK-188

from confluence with Silver Cr. (S16 T94N R5W Clayton Co.) to confluence with unnamed tributary in S8 T95N R6W Clayton Co.

Assessment Cycle
2004
Result Period
2000 - 2002
Designations
Assessment Methodology
Assessment Type
Monitored
Integrated Report
Category 5b
Legacy ADBCode
IA 01-TRK-0360_3
Overall Use Support
Partial
Aquatic Life Use Support
Partial
Documentation
Assessment Comments

Assessment based on results of (1) IDNR/UHL biolgoical (REMAP) sampling in 2002 (Fish IBI= 48 (fair), BM-IBI= 61(good) and (2) IDNR/UHL biological (biocriteria) sampling in 2000 (Fish IBI= 51 (good); BM-IBI= 59 (good)).

Basis for Assessment

SUMMARY:  The Class B(LR) aquatic life uses are assessed (monitored) as "partially supported"  based on results of IDNR/UHL biological sampling in 2000 and 2002.  

EXPLANATION:  This assessment was based on data collected in 2000 and 2002 as part of the DNR/UHL stream biocriteria and REMAP projects, respectively.   A series of biological metrics which reflect stream water quality and habitat integrity were calculated from the biocriteria sampling data.   The biological metrics are based on the numbers and types of benthic macroinvertebrate taxa and fish species that were collected in the stream sampling reach.   The biological metrics were combined to make a fish community index of biotic integrity (F-IBI) and a benthic macroinvertebrate index (BM-IBI).   The indexes rank the biological integrity of a stream sampling reach on a rising scale from 0 (minimum) to 100 (maximum).   The 2002 Fish IBI score was 48 (fair) and the BM-IBI score was 61 (good).   The 2000 Fish IBI score was 51 (good) and the BM-IBI score was 59 (good).  The aquatic life use support was assessed as partially supporting (=PS), based on a comparison of the F-IBI and BM-IBI scores with biological assessment criteria established specifically for the 2002 Section 305(b) report.  The Fish IBI scores were slightly below the biological assessment criterion, which was determined from a statistical analysis of data collected at stream ecoregion reference sites from 1994-2001.

As part of the 2002 REMAP sampling project, stream physical habitat assessment found adverse conditions that are thought to contribute to the biological impairment.   These include, bank instability, excessive silt deposition, and removal of riparian vegetation associated with livestock grazing.   High silt levels were also observed during physical habitat assessment of the 2000 sample site.

Monitoring and Methods
Assessment Key Dates
7/31/2002 Biological Monitoring
7/31/2002 One-time Chemical Monitoring
8/1/2000 Biological Monitoring
8/1/2000 One-time Chemical Monitoring
Methods
220 Non-fixed station physical/chemical monitoring (conventional pollutant only)
315 Regional reference site approach
320 Benthic macroinvertebrate surveys
330 Fish surveys
380 Quan. measurements of instream parms-- channel morphology-- floodplain-- 1-2 seasons-- by prof
Monitoring Levels
Biological 4
Habitat 4
Physical Chemistry 1
Toxic 0
Pathogen Indicators 0
Other Health Indicators 0
Other Aquatic Life Indicators 0
# of Bio Sites 1
BioIntegrity Good
Causes and Sources of Impairment
Causes Use Support Cause Magnitude Sources Source Magnitude
Other habitat alterations Aquatic Life Support Moderate
  • Agriculture
  • Bank or Shoreline Modification/Destabilization
  • Hydromodification
  • Removal of Riparian Vegetation
  • Moderate
  • Moderate
  • Moderate
  • Moderate
Siltation Aquatic Life Support Moderate
  • Agriculture
  • Bank or Shoreline Modification/Destabilization
  • Hydromodification
  • Moderate
  • Moderate
  • Moderate